Classifications

• • A—HUMAN NECESSITIES
  • A62—LIFE-SAVING; FIRE-FIGHTING
  • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
  • A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
  • A62D3/30—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
  • A62D3/38—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by oxidation; by combustion
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
  • B01D—SEPARATION
  • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
  • B01D53/34—Chemical or biological purification of waste gases
  • B01D53/46—Removing components of defined structure
• • A—HUMAN NECESSITIES
  • A62—LIFE-SAVING; FIRE-FIGHTING
  • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
  • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
  • A62D2101/40—Inorganic substances
• • A—HUMAN NECESSITIES
  • A62—LIFE-SAVING; FIRE-FIGHTING
  • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
  • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
  • A62D2101/40—Inorganic substances
  • A62D2101/43—Inorganic substances containing heavy metals, in the bonded or free state
• • A—HUMAN NECESSITIES
  • A62—LIFE-SAVING; FIRE-FIGHTING
  • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
  • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
  • A62D2101/40—Inorganic substances
  • A62D2101/45—Inorganic substances containing nitrogen or phosphorus
• • A—HUMAN NECESSITIES
  • A62—LIFE-SAVING; FIRE-FIGHTING
  • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
  • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
  • A62D2101/40—Inorganic substances
  • A62D2101/47—Inorganic substances containing oxygen, sulfur, selenium or tellurium, i.e. chalcogen

Definitions

• the present invention relates to a method for the removal of non-metal and metalloid hydrides from gas and liquid media.
• Non-metal hydrides such as phosphine, and metalloid hydrides such as arsine and germane, can occur as unwanted constituents in a number of gas or liquid process streams. These materials are highly toxic and can present a severe personal and environmental hazard even at concentrations of less than a few parts-per-million.
• hydrides are used directly in large quantities as dopants in the manufacture of semi-conductor materials.
• Other uses include their use as fumigants and biocides in various agricultural applications. They may also arise as unwanted contaminants in other process streams where their use per se is unintended.
• arsine and phosphine fumes may arise in the process off-gases due to the presence of trace amounts of arsenic and phosphorus in the unrefined metals.
• Adsorption systems are inherently more convenient to operate since they usually require very little maintenance and no chemical additions. For this reason their use may be preferred where they can be made to be economically viable.
• the adsorption of a hydride on an activated carbon is usually physical in nature, preserving the chemical identity of the hydride.
• the physical adsorption capacities of some hydrides is limited, requiring large amounts of activated carbon for their effective removal by physical adsorption alone.
• the hydride can be converted chemically into a compound which adsorbs more strongly on the carbon surface, removal of the hydride can be enhanced.
• the presence of an oxidant such as oxygen may allow conversion of the hydride into the corresponding oxide which is much more strongly adsorbed by the carbon. Even then, the rate and extent of conversion of the hydride may be insufficient.
• activated carbons impregnated in this manner also possess several inherent disadvantages which may limit their overall utility. These disadvantages include the high costs of some impregnants such as silver, lowered carbon ignition temperatures, impregnant toxicity and attendant disposal limitations, and diminished ability to regenerate or reactivate the spent carbon once it has become exhausted for hydride removal. The added metals may also occupy adsorption pore volume that is now lost for the physical adsorption of other compounds which may also be present in the process stream and require removal.
• the present invention comprises a method for the removal of metalloid and non-metal hydrides from gas and liquid media such as air, in the presence of an oxidant such as oxygen, by contacting said media with a nitrogen-treated carbon or carbonaceous char.
• an oxidant such as oxygen
• the spent carbon or char may be regenerated simply by washing the spent char with water. The recovered products may then be reclaimed for additional uses or disposed of in an environmentally-acceptable manner.
• any other suitable solvent may be used provided this solvent can be conveniently removed from the carbon surface after contact with the spent carbon.
• Additional recovery of the initial hydride removal capacity of the carbon may be achieved by reactivating the spent carbon. Reactivation is generally accomplished by heating the spent carbon to high temperatures, typically above about 700* C, in the presence of one or more of an inert gas, steam, carbon dioxide or oxygen. To avoid the appearance of excessive amounts of reduced non-metals or metalloids in the reactivation off-gasses, regeneration is carried out prior to high-temperature reactivation. Reactivation is recommended in those instances where adsorbable organics or other materials which poison the sites specific for hydride removal gradually diminish the activity of the carbon after each regeneration cycle until a point is reached where the carbon can no longer function effectively.
• an oxidant containing process stream such as air, containing a hydride such as phosphine
• a carbonaceous char which has been previously exposed at temperatures above about 700* C to a nitrogen-containing compound such as urea.
• the process stream can be contacted with a carbonaceous char which has been previously derived from a nitrogen-rich feed stock such as polyacrylonitrile, polyamide, or any of a variety of organic amines.
• the resultant char can be activated at high temperatures, typically above 700* C, with any of steam, carbon dioxide, or oxygen to impart suitable transport and adsorption properties to the char prior to its contact with the process stream. These properties may vary depending on the conditions of a particular application.
• the spent char may then be regenerated by washing it with a suitable solvent such as water. If the performance of the char after regeneration is no longer acceptable, the char may be additionally reactivated at high temperatures, typically above 700* C, to restore its hydride-removal capacity.
• the char which is contacted with the hydride-containing process stream is prepared by the low-temperature carbonization and extensive oxidation of a nitrogen-poor carbon feed stock.
• the material which results from the carbonization and oxidation process is then subjected to a nitrogen-containing compound such as urea as the temperature is raised to above 700* C to produce a high temperature carbonaceous char.
• a nitrogen-containing compound such as urea as the temperature is raised to above 700* C to produce a high temperature carbonaceous char.
• high-temperature carbonaceous chars are those produced by thermal treatment at temperatures greater than 700* C.
• Low-temperature carbonaceous chars are those which have not experienced temperatures greater than 700* C.
• the preferred nitrogen-poor carbon feed stock is a bituminous coal or a material having bituminous properties such as those derived from higher or lower rank bitumens, coals, or lignocellulose materials by various chemical treatments ("bituminous-materials") .
• bituminous-materials include anthracite or semi-anthracite coals, while examples of lower rank coals include peat, lignite, and sub-bituminous coals.
• Examples of the chemical treatment of these feed stocks include alkali metal treatment of the high rank materials and zinc chloride or phosphoric acid treatment of the low rank materials. These types of treatments can also be applied to lignocellulose materials.
• the feed stock material is pulverized, mixed if necessary with small amounts of a suitable binder such as pitch, briquetted or otherwise formed, and sized.
• the sized material is then extensively oxidized at temperatures less than 700* C, preferably less than 400* C.
• the oxidation is continued until additional gains in the catalytic activity of the final product are no longer evident.
• the oxidation is well beyond that typically required to remove the coking properties of bituminous coals and produces an optimally oxidized char.
• Other convenient means of oxidation can also be used to effect the low-temperature oxidation and carbonization of the starting material.
• the oxidized low-temperature carbonaceous char is then exposed to small amounts of an inexpensive, abundant, and relatively nontoxic nitrogen-containing compound such as urea, ammonia, melamine or any other nitrogen-containing compound in which at least one nitrogen functionality has a formal oxidation number other than zero.
• the amounts of nitrogen-containing compounds used are typically small, preferably less than 5% by weight of the oxidized low-temperature carbonaceous char or such that additional gains in the catalytic activity of the final product are no longer evident.
• the heating is preferably conducted under an atmosphere that is inert except for the gases and vapors attributable to the char and/or the nitrogen-containing compounds.
• the heating rates and temperatures are preferably selected such that additional gains in the catalytic activity of the final product are no longer evident.
• Theresultantnitrogen-treatedhigh-temperaturecarbonaceous char may then be activated to the desired density at temperatures above 700* C in steam and/or carbon dioxide, with or without the addition of other gasifying agents such as air.
• the activated char is then cooled in an oxygen-free or otherwise inert atmosphere to temperatures less than 400* C, preferably less than 100* C.
• Additional gains in hydride-removal activity may be realized by repeating any or all of the aforesaid steps as many times as may be desired.
• any other known method in which a carbonaceous char is treated with nitrogen-containing compounds at high temperatures may be applied to the resultant product to further enhance its activity.
• Example 1 provides a representation of prior art practices
• Example 2 provides a representation of the preferred embodiment of the present invention. Comparison of the results of Example 1 to those of Example 2 clearly shows the advantage achieved by the present invention.
• a one-inch diameter column was filled to a depth of twelve inches with BPL carbon (Calgon Carbon Corporation, Pittburgh, PA) .
• BPL carbon is a commercially-available bituminous coal-based activated carbon.
• the particular sample used for this experiment was screened to a strict 4x6 mesh (U.S. Standard Series Sieve) and had an Apparent Density (Test Method TM-7, Calgon Carbon Corporation, Pittsburgh, PA) of 0.507 grams per cc.
• a 50% relative humidity nitrogen stream containing 200 ppm phosphine and 500 ppm oxygen was then passed up flow through the column at a flow velocity of 50 feet per minute.
• the phosphine concentrations of the effluent from the column were then measured. After 8 hours of operation the phosphine concentration in the effluent from this column measured 88 ppm.
• the percentage of phosphine removed equalled 56%.
• Bituminous coal was pulverized, mixed with about 4% to 6% coal tar pitch, and briquetted.
• the resultant briquettes were crushed and sized to produce an approximately less than 4 mesh and greater than 10 mesh (U.S. Standard Series sieves) material.
• this material was carbonized and oxidized at temperatures between about 250* C and 450° C for at least 3 hours.
• the resultant oxidized char was cooled to near ambient temperatures and subsequently impregnated with an aqueous urea solution and dried. The quantity of urea solution used was sufficient to produce a 2%-4% urea loading on a dry weight basis.
• the impregnated, oxidized char was then heated to about 950" C in a furnace and maintained at that temperature for up to 1 hour.
• the material was contacted with steam, while maintaining a 950* C temperature, for a period of time sufficient to achieve an Apparent Density (Test Method TM-7, Calgon Carbon Corporation, Pittsburgh, PA) of about 0.51 grams per cc for a 4x6 mesh (U.S. Standard Series sieves) particle size distribution.
• the material was cooled to ambient temperature under an inert atmosphere.
• the nitrogen-treated carbon produced by this procedure was then screened to a strict 4x6 mesh.
• the Apparent Density of this material was determined to be 0.514 grams per cc.
• a one-inch diameter column was filled to a depth of twelve inches with the carbonaceous char prepared as described above.
• a 50% relative humidity nitrogen stream containing 200 ppm phosphine and 500 ppm oxygen was then passed up flow through the column at a flow velocity of 50 feet per minute.
• the phosphine concentrations of the effluent from the column were then measured. After 8 hours of operation the phosphine concentration in the effluent from this column measured less than 2 ppm.
• the percentage of phosphine removed was greater than 99%. While the presently preferred embodiments of the invention have been described in particularity, they may be otherwise embodied within the scope of the appended claims.

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• 1994
  • 1994-07-25 US US08/279,783 patent/US5674462A/en not_active Expired - Lifetime
• 1995
  • 1995-07-25 AT AT95928363T patent/ATE209065T1/de not_active IP Right Cessation
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  • 1995-07-25 DK DK95928363T patent/DK0772486T3/da active
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